Appendix 1 Management of the Highgate and Hampstead Ponds Introduction This report summarises the proposed management of the Highgate and Hampstead Ponds following completion of the Hampstead Heath Ponds Project. It does not cover management of the wildflower meadows on Tumulus and Pryors Fields. Part 1 describes the new Ponds Project habitats and outlines what management is required, both during establishment phase and subsequently, to maintain them. Part 2 considers management of the ponds which is unrelated directly to the Ponds Project. Part 1: the new Ponds Project habitats and their management A range of new habitats have been created through the Ponds Project; this section describes them and outlines their proposed management. Their locations are listed in Table 1 below and they are mapped schematically in figures 1 and 2. The new habitats Marginal vegetation Beds of marginal emergent vegetation now line edges of ten ponds, adding nearly two hectares of wetland planting to the Heath. They are composed of reed alone; of reed plus other marginal plants such as sedges and purple loosestrife; or of marginal plants without reed. The beds of vegetation are currently fenced to prevent access to people, dogs and waterfowl; the latter would graze the vegetation and prevent good establishment. Marginal vegetation is a very important wildlife habitat which had been substantially lacking from the Heath’s ponds. It benefits a wide variety of species, including fish, birds, invertebrates and amphibians, harbours beneficial microorganisms and also filters the water, maintaining good water quality. The plants also soften the appearance of the ponds, creating a more attractive and natural look. Pools and scrapes and streams Pools and wetland scrapes were created above the Ladies Pond, at the Bird Sanctuary and south of the Catchpit dam, and a new embayment was made at the Bird Sanctuary to extend the reedbed. These will all provide excellent habitat for wetland wildlife. About 60 metres of stream formerly piped below ground were brought to the surface. Aerators Aerators have been installed in all the ponds and these will also improve water quality by raising oxygen levels, especially in warm weather, and reducing algal growth. Page | 1 Grassland and wild flowers Most of the grassland of Hampstead Heath is heavily dominated by grasses, and disappointingly lacking in ‘wild flowers’. The Ponds Project sought to increase species diversity where possible. It was a requirement of the Supervising Engineer that turf was layed on the spillways and most of the dam faces, and a special turf was used which contained 20% wild flowers seeds 80% native grasses. It is also a requirement that the dam faces and spillways be mown sufficiently frequently to maintain a relatively short sward, and this, as well as public pressure, will reduce the number of plants flowering. However, the lower-growing species, such as red clover and bird’s-foot trefoil, should be able to bloom where footfall is not too great, providing nectar for bees, moths, butterflies and other insects. A herb-rich seed mix was used instead of turf on the slopes of the Boating Pond Island; this does not require frequent mowing. Over 600 wild flower plugs and bulbs were planted at Stock and Hampstead no. 1 Ponds. Further planting of wild flowers is anticipated at the Ladies Pond. Trees and shrubs About 50 trees and 130 shrubs were planted, many of them close to ponds. All are native species apart from two London planes replacing two which had to be felled at Hampstead No. 2. They included oak saplings which were transplanted from the Heath, maintaining local provenance, and elms which are resistant to the Dutch Elm Disease which ravaged the tall elm trees common on the Heath until about the 1970s. The new trees will provide landscape and wildlife benefits. Hibernacula, wood piles and bat boxes Two amphibian and grass snake hibernacula were built at the Bird Sanctuary, and brash and log piles were constructed by four Ponds. Twelve bat boxes were put up a further eight are to be added in early spring 2017; some of these are near ponds. De-silting Silt was removed during the Ponds Project from the Stock, Ladies, Men’s, Viaduct and Mixed Bathing Ponds. The Viaduct Pond was particularly badly silted, with especially shallow water even threatening the continued existence of the northern section. The substantial amounts of silt and logs which were removed should result in notable improvements to the ecology of this pond. Page | 2 Table 1: Summary of new pond-related habitats by location Marginal Flowery turf Wildflower Tree / shrub Wildflower Trees Hibernacula and Streams, channels, Other Location vegn, m2 on dams and meadows planting plugs and and brash and wood pools and scrapes approx. spillways etc. bulbs shrubs piles Stock Pond 44 √ √ Brash/wood piles Section of stream brought above ground Ladies Pond 40 √ √ √ (planned) √ Pools and scrapes Bird 2 hibernacula plus Scrapes and 30m of New embayment Sanctuary log piles new channel for reedbed expansion Boating 670 √ √ (island √ √ Pond slopes) Men’s Pond 228 √ √ √ New wet bay at NW corner Highgate no. 96 √ 1 Pond Vale of 40 √ Brash/wood piles Health Pond Viaduct Pond 56 √ √ √ Rock rolls installed to hold back marsh By Catchpit 10 √ √ √ New seasonal pond; New silt trap Dam section of steam brought above ground Mixed Pond 208 √ √ √ Brash/wood piles Rock rolls to hold back marsh Hampstead 94 √ √ Further small no. 2 Pond reedbed to be planted near platform Hampstead 276 √ √ √ √ no. 1 Pond Other 12 bat boxes installed near ponds, 8 more to be added Page | 3 Figure 1: The new Ponds Project habitats on the Hampstead chain of ponds (not to scale) Page | 4 Figure 2: The new Ponds Project habitats on the Highgate chain of ponds (not to scale) Page | 5 Management of the new ponds-related habitats Monitoring All the new habitats need to be monitored, so that any problems can be addressed, such as weed growth and plants or seed mixes failing to establish. Walk-over surveys will be made during the establishment phase; detailed quadrat surveys may be more useful later on. The on-going long-term programme of monitoring of amphibians will be extended to suitable new wetland habitats. Water quality is monitored regularly in all the ponds affected by the Ponds Project. Visual checks are made weekly throughout the year, and oxygen levels are measured weekly during the warm months. This programme will be continued. A fuller baseline survey was undertaken in 2013, before works began, and this should be repeated in 2020/21 or soon afterwards to assess the impact of the works on water quality, macro-invertebrates and aquatic macrophytes. Marginal vegetation In the first 1-2 years, any gaps in the aquatic vegetation will need to be replanted by the contractor. Both the land and water sides of the beds of marginal plants are currently fenced to prevent access by dogs, people and water birds, apart for two gaps at the Boating Pond cut to allow access to the island for swans. The landward fences will need to be retained, but ideally some fencing on the water-side of the wetland areas should be opened up or removed once the vegetation is established. However, caution is required: fencing round the older reed beds on the Boating Pond was temporarily taken away some years ago, resulting in serious erosion of the vegetation by dogs and water birds, and the fence had to be replaced. As a trial, in 2017 it is proposed to open up panels in waterside fencing where the vegetation is well established, for example at the Men’s Pond. If this does not result in too much damage from grazing by birds further panels will be removed. Over the years, plant remains will gradually build up in the reedbeds, raising the soil levels. This is a natural process: shallow reedbeds are not permanent habitats and dry out unless managed. The habitat is degraded as the aquatic vegetation loses its vigour and is gradually replaced by plants of drier places, such a willow and alder, resulting in a loss of value to wildlife, such as amphibians and aquatic invertebrates. Thus a long term programme of occasional rotational cutting back the vegetation, removing inappropriate species such as shrubs and trees. Eventually re-excavating the reedbeds will be needed. At this stage is it impossible to determine just when this will first be necessary or the required frequency, but for comparison the regime for the Bird Sanctuary reedbed is an 8-year rotation. Streams, channels, pools and scrapes From time to time open water will need to be maintained in channels, pools and scrapes by removal of some of the vegetation as required. Silt removal will also be needed to maintain water depth, especially in the shallower features. A slow flow of water is ideal to reduce erosion and sedimentation. Aerators Page | 6 Aerators will be maintained in good working order. They will be turned on as required when water quality has been or is likely to decline, e.g. in hot weather or after heavy rainfall. Wild flower turf, seeded areas and plugs The Supervising Engineer has specified a complex regime for cutting the wildflower turf laid on the spillways and dams. This varies from a single cut in late spring/early summer to up to ten cuts through the growing season, every time the grass reaches 175mm in height. It is hoped that this programme can be rationalised and the frequency reduced in some places. The slopes of the Boating Pond Island were seeded with grass and wild flowers. Careful management will be needed in the first couple of years, 2017 and 2018.